Lessons on cooperation building to manage water conflicts in the Aral Sea Basin; Technical documents in hydrology: pc-cp series; Vol.: 11; 2003


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Indicators 
Kazakh-
stan 
(south) 
Kyrgyz 
Republic 
Tajik-
istan 
Turkmen-
istan 
Uzbek-
istan 
Needed operational 
costs 
32.0
115.50
117.0

139.0
575.0 
Actual operational 
costs, 
including: 
1.6 5.28
9.75 39.8
392.0 
budget financing 
0.32 3.40
7.10 39.8
392.0 
water users’ fee 
1.28 
1.88 
2.56 
– 
– 
Actual operational 
costs as % of demand 
5.0 4.60
8.30 18.8 68.1 
Specific needed costs,
$ per ha
111.3
108.90 162.00 127.9 
137.0 
Specific actual costs, 
$ per ha
5.6
5.00
13.50 
24.0 
93.3 
Note: All figures in million $US.
Services for maintenance and repair of the on-farm irrigation and collector-
drainage network could by provided by state water divisions or by associations of 
water users (WUA). In all cases the water users pay for these services. 
In Soviet times capital investments in the water sector, including water resource 
conservation and land reclamation, were funded by the federal government as well as 
republican budgets. The current financial status of the Central Asian states has led to 
a reduction of investment in the water sector. It is worth noting that investment rates 
differ sharply for different countries depending on government commitment and 
financial status. 
The agricultural sector in all of the countries needs state support or subsidies. 
This can be justified in cases where the state regulates the price of the main 
agricultural products such as cotton and grain, which are sold to the state for fixed 
prices which are lower than world market ones. All the Central Asian states recognize 
the need to charge for water. Payments for water use not only solve the economic 
problems of water organizations, but facilitate better management, rational water use, 
and water saving in all branches of the economy. 
All the states need to decide on legally enforceable charges for pollution. The 
level of pollutants released in water sources needs to be determined by interstate 
agreements with sanctions applied to particular states when these limits are 
exceeded. Provisions for payment for pollution, release of substances at higher than 
permitted concentrations, excessive water use, restrictions on water transfer, and 
similar regulations should be coordinated by interstate agreements that set criteria for 
water allocation and use, and are based on the following well-known principles: 
● 
the previous user presumption 
● 
the “do no harm” rule 
● 
equitable and reasonable water use. 
At the national level it is proposed to establish charges for waste produced by non-
irrigation consumers related to pollutant concentration. Using funds raised by fines for 
23 


release of pollutants to the rivers and tributaries in excess of permitted limits, or for 
exceeding the permitted concentration of toxic elements, it is hoped to create national 
ecological water funds to finance “clean technologies” and improve the ecological state 
of rivers and water bodies. 
Water users who have licenses for guaranteed quantities of water could transfer 
(sell) any surplus part of their quotas, or the entire quota, to other users in mutually 
beneficial transactions. The main factor that could make this possible could be the use 
of water-saving technology. This method could be especially effective at WUA level. In 
the Kyrgyz Republic, in particular, official government policy predicates that, where 
use of irrigation water is reduced by using up-to-date technologies, the WUA has a 
right to sell the saved water at market prices. Trade rights should be provided to 
water-related organizations that invest in water-saving measures and additional water 
resources involvement. Other prospects for promoting water saving at the WMO level 
entail bonus payments to staff of the organization related to permanent expenses per 
cubic meter of water delivery cost. 
Contrary to the provisions of existing law, which ignores public participation, new 
laws should initiate the creation of public bodies of stakeholders for the institutional 
and financial framework of water management. 
Common tasks for developing economic mechanisms for the water sector and for 
implementing them at the interstate level are as follows: 
● 
to provide sustainable mechanisms for financing and maintaining interstate water 
resource management systems and interstate bodies 
● 
to create incentives for all states and water users to conserve water and to 
ensure it is available to meet environmental needs 
● 
to apply the “polluter pays” principle in practice 
● 
to create a mechanism to balance benefits and costs at the level of interstate 
water distribution and use. 
There are no strict financial obligations on states to engage in joint water 
management and development. Although the operational budget is confirmed each 
year by a decision of the ICWC before the beginning of the fiscal year, only 
Turkmenistan and Uzbekistan have fully met their obligations to pay for operational 
requirements and repair work. As for research work, only Uzbekistan has fully met its 
obligations, with very small contributions from the other states. Attempts to facilitate 
the financing of reconstruction and development have met opposition from all the 
states’ financing bodies. As a result only a small part of the required reconstruction 
works for hydrometeorological services on transboundary rivers and for one headwork 
in BWO has been done. 
Some new financial measures for interstate relations are now being considered 
or are in their preparatory phase. One of these is a proposal to share water and power 
supplies on the Syr-Darya river by implementing charges for the volume of water to 
be delivered to lowland states as a result of water regulation; the charges might be 
seasonal or multiyear. The amount charged per unit of water to water users below 
reservoirs must cover the running expenses for collecting and conserving this volume. 
The charge must also compensate for the “lost benefit” of water release through 
dams, which might otherwise have been used for energy generation. Of course, prices 
charged under seasonal regulation are often less than prices under multiyear 
regulation. 
Another of these measures relates to negotiations about the creation of a 
“Water–Power Consortium,” as a financial body that will determine more efficient 
options for power exchanges and allocation among users, bearing in mind the best 
interests of local authorities. 
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A third measure is to divide funding responsibilities for hydrometerological, 
geological, and other facilities among water users in proportion to the volumes 
consumed. 

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